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Natural regeneration of alpine tundra vegetation after human trampling: A 42-year data set from Rocky Mountain National Park, Colorado, USA

机译:踩踏后高山苔原植被的自然再生:来自美国科罗拉多洛矶山国家公园的42年数据集

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The vegetation composition of four contiguous permanent plots was analyzed during 37 of 42 years between 1959 and 2001 to evaluate successional processes following the cessation of human trampling in alpine tundra. The plots were established adjacent to the Rock Cut parking lot at similar to 3658 m elevation along Trail Ridge Road in Rocky Mountain National Park, Colorado. Due to limitations in the original study design, the lack of true replication required that the plots be treated individually when subject to indirect ordination analysis to follow trends in overall plant composition and cover. The three most abundant species in the study plots were Artemisia scopulorum, Acomastylis rossii, and Kobresia myosuroides. At the beginning of the study in 1959, total cover ranged from 20 to 55% in the four plots. By 1961, three of the four plots achieved total canopy cover values of at least 100%. Vascular plant species richness (number of taxa per plot) averaged 20 in 1959, but by 1967 had nearly doubled to 37. During the first several years, rates of seedling emergence were high among most taxa with the notable exceptions of K myosuroides and A. rossii. However, likely due to desiccation and needle ice, seedling mortality was high. K myosuroides spread exclusively from remnant tufts, as did three species of cushion plants which survived the trampling. The overall decline in plant cover during the last two decades of this study, particularly for K myosuroides, indicates that long-term unassisted regeneration of severely degraded alpine tundra sites will take more than a century. While there have been periods of plant colonization and spread, climate factors such as a series of heavy snow years, and unchecked soil erosion from trails, can limit plant establishment and stop the recovery process, or push the recovery back by several decades. The negative influence of soil erosion, and quite possibly additional trampling, over a significant portion of the study plot points to the critical importance of using extreme care when establishing long-term monitoring plots, particularly in high-use areas.
机译:在1959年至2001年之间的42年中的37年中,对四个连续的永久性地块的植被组成进行了分析,以评估在高山冻原上停止践踏人类后的演替过程。该地块是在Rock Cut停车场附近建立的,沿科罗拉多洛矶山国家公园的Trail Ridge Road海拔3658 m。由于原始研究设计的局限性,缺乏真正的重复性要求对地块进行间接排序分析时要进行单独处理,以遵循总体植物组成和覆盖率的趋势。研究区中三个最丰富的物种是苦艾蒿,罗汉果(Acomastylis rossii)和小嵩草(Kobresia myosuroides)。 1959年研究开始之初,在四个样地中,总覆盖率在20%至55%之间。到1961年,四个地块中的三个地块的总冠层覆盖率至少达到100%。 1959年,维管束植物物种丰富度(每样地的分类单元数量)平均达到20种,但到1967年,几乎增加了一倍,达到37种。在最初的几年中,大多数分类单元中的幼苗出苗率都很高,但值得注意的是肌硫磷和A。罗西然而,很可能由于干燥和针状冰,幼苗死亡率很高。 Myosuroides钾仅从残留的簇中传播,幸存下来的三种缓冲植物也是如此。在这项研究的最后二十年中,植物覆盖率总体下降,尤其是对神经硫磷钾而言,表明严重退化的高山苔原站点的长期无辅助再生将需要一个多世纪。尽管存在植物定植和扩散的时期,但气候因素(例如一系列的大雪年以及径迹不受控制的土壤侵蚀)可能会限制植物的生长并阻止恢复过程,或将恢复推迟数十年。土壤侵蚀的负面影响以及相当可能的其他践踏对研究区的很大一部分都表明,在建立长期监测区时,尤其是在高使用地区,使用极端护理至关重要。

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